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Tiêu đề Nutrient Management: Diet Modification
Tác giả Terry J. Klopfenstein
Trường học University of Nebraska
Chuyên ngành Animal Science
Thể loại Essay
Thành phố Lincoln
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Số trang 17
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Values shown in Table 1 illustrate the nutrient content in different manure storage systems but do not represent the full range of variation within a species or among manure storage syst

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Nutrient Management: Diet Modification

Terry J Klopfenstein

University of Nebraska, Lincoln, Nebraska, U.S.A

INTRODUCTION

Animal feeding operations are becoming more

concen-trated and the U.S EPA (Environmental Protection

Agency) has proposed more restrictive requirements

Great progress has been made in diet modifications

designed to reduce animal excretion of nutrients The

nutrients of primary concern are nitrogen and phosphorus

PHOSPHORUS UTILIZATION

Phosphorus (P) is an essential mineral nutrient required

for bone growth and maintenance and for most body

metabolic functions such as energy utilization

Phospho-rus has been supplemented to animal diets in mineral form

such as dicalcium phosphate produced from mined

mineral deposits Typically, phosphorus was fed above

the requirement of the animals as a safety factor due to lack

of confidence in the precise P requirements and supplies P

in manure can build up in soils and subsequently

con-taminate ground water if not properly managed P

require-ments are quite different for ruminants (cattle and sheep)

and nonruminants (pigs and chickens), and P is

metabo-lized differently by ruminants

Poultry and swine grow rapidly and therefore require

high levels of P in their diets (up to 6% of diet;[1–3])

Much of the P in feed ingredients (such as corn and

soybean meal) is in the form of phytate P Swine and

poultry lack the enzyme (phytase) necessary to utilize the

phytate P so it appears in the manure Inorganic P must be

supplemented to meet the animal’s requirements This

makes P use very inefficient (10 to 20%) and most of the P

ends up in the manure There are four technologies that

producers can use to reduce P excretion

1 Feeding to requirements Ongoing research is helping

to more precisely define P requirements for each

type of production and for animal ages within each

type of production With modern technology, it is

possible to formulate diets quite precisely so that P is

not overfed.[1]

2 Phytase This enzyme is produced commercially

through microbial fermentations and can be added to

swine or poultry diets Phytase releases the organic P from phytate and makes it available to the animal.[4,5] Therefore, the phytate P in corn and soybeans, the primary feedstuffs in swine and poultry diets, is utilized to meet the animal’s requirements, reducing the need for supplement

3 Phase feeding Swine and poultry grow rapidly Bone growth is very rapid in young animals and is essentially zero in mature animals Therefore, the requirement for P decreases as the animals grow and mature.[2,3] Phase feeding is the process of changing diets to reduce the amount of P In the past, two or three diets may have been fed, but now the number is increasing to five or six Phase feeding, combined with precise formulation and precise requirements, decrease dietary P and therefore manure P.[1]

4 Low phytate feeds Genetically enhanced low-phytate corn and soybean meal are available The total P in these feedstuffs is not necessarily lower, but the P is in the available, inorganic form rather than the organic (phytate) form.[1,6] Feeding low-phytate corn and soybeans can decrease P excretion by 50%

Beef and dairy cattle digest and metabolize P somewhat differently than nonruminants The microorganisms in the rumen digest the P in phytate, making the P available to the animal Beef and dairy cattle tend to grow slower and have lower P requirements than nonruminants.[7,8] Lac-tating dairy cows excrete considerable amounts of P in milk so cows giving milk have higher requirements higher requirements for higher producers.[8]

The most important issue with ruminants is to establish precise requirements and then formulate diets to meet but not exceed requirements The requirements for lactating dairy cows is about 30% of the diet.[9] The ingredients (corn, supplemental protein, silage, alfalfa) fed to dairy cows will supply most, if not all, of this requirement Beef cattle in feedlots are typically fed diets high in corn grain, which contains 25 to 3% P Recent research suggests the requirement for feedlot cattle is 12 to 14%.[10]The problem is that the ingredients in the feedlot diets (primarily corn) have nearly 3% P There does not seem to be any practical way of reducing dietary P levels below 25% and therefore, P excretion by feedlot cattle is relatively high

DOI: 10.1081/E EAS 120019731 Copyright D 2005 by Marcel Dekker, Inc All rights reserved.

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NITROGEN UTILIZATION

Nitrogen (N) is a part of amino acids (AA) that form

proteins required by all animals; animals consume protein

and AA and then excrete various forms of N If N in

manure is not managed appropriately, it can contaminate

surface and ground waters (nitrate) Just as important is

the volatilization of N (NH3) from manure The resulting

NH3(ammonia) adds to odors and can be redeposited on

cropland or environmentally sensitive areas such as lakes

and streams

Swine and poultry must be fed essential AAs to meet

requirements Because of rapid lean growth, AA

require-ments are high and must be met to produce optimal body

weight gains and feed efficiencies.[2,3] However, if any

AA is fed above the requirement, that AA will be used for

energy and the N excreted

IDEAL PROTEIN

The ideal protein is a protein with a balance of amino

acids that exactly meets an animal’s AA requirements.[11]

By formulating diets to ideal protein content, no excess

AAs are fed and N excretion is minimized Formulation

for ideal protein can be accomplished by using

high-quality protein sources with good balances of AA and

protein sources that complement the AA balance in corn

The greatest opportunity is to use crystalline AA to

bal-ance for AA deficiencies Lowering the dietary protein

content by two percentage points and supplementing with

crystalline AA results in a 20 to 25% decrease in N

ex-cretion in swine or 30 to 40% in poultry.[12]

FEED ADDITIVES

Feed additives or feeding management systems that

in-crease feed efficiencies also inin-crease efficiency of N

uti-lization Ractopamine increases lean growth in swine and,

therefore, increases N-use efficiency.[1]

PHASE FEEDING

Amino acid requirements decrease as swine and

poul-try grow, just as the P requirement decreases Balancing

diets to ideal protein and changing diets often as pigs or

poultry grow decrease the protein fed and, therefore, the

N excreted.[1]

NITROGEN FOR RUMINANTS Cattle are unique because of the microflora in the rumen This ability allows them to digest fiber, but does raise some challenges in protein nutrition Protein that reaches the small intestine is a combination of microbial protein and undegraded feed protein This protein (metabolizable protein, MP) is digested and absorbed in a manner similar

to nonruminants The growing beef animal and lactating dairy cows have two requirements that nutritionists must meet degradable protein for the rumen microbes and undegraded protein that supplies the additional MP needed by the animal.[7,8] Only recently have these requirements been elucidated, and further refinement of requirements is needed

The greatest opportunity for decreasing N excretion by cattle is to use the MP system to meet but not exceed requirements for degradable and undegradable protein Phase feeding feedlot cattle and group feeding dairy cows have the potential to markedly reduce N excretion Ammonia losses have been reduced by as much as 32%

by using these technologies.[13]There is some reluctance

by nutritionists to reduce levels of degradable and undegradable protein because of concern that milk or beef production will be compromised Research indicates that will not happen, but it is more difficult to control variables in commercial production facilities.[14–16]

CONCLUSION Phosphorus and nitrogen excretion can be reduced markedly by the use of new technologies In the future, there will be incentives for producers and nutritionists to make use of these technologies

REFERENCES

1 Klopfenstein, T.J.; Angel, R.; Cromwell, G.L.; Erickson, G.E.; Fox, D.G.; Parsons, C.; Satter, L.D.; Sutton, A.L Animal Diet Modifications to Decrease the Potential for Nitrogen and Phosphorus Pollution; Council for Agricul tural Science and Technology: Ames, IA, 2002 CAST Issue Paper Number 21

2 National Research Council Nutrient Requirements of Poultry, 9th Ed.; National Academy Press: Washington,

DC, 1994

3 National Research Council Nutrient Requirements of Swine, 10th Ed.; National Academy Press: Washington,

DC, 1998

4 Kornegay, E.T.; Denbrow, D.M.; Yi, Z.; Ravindran, V Response of broilers to graded levels of microbial phytase

Nutrient Management: Diet Modification 665

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added to maize soybean meal based diets containing three

levels of non phytate phosphorus Br J Nutr 1996, 75,

839 852

5 Cromwell, G.L.; Stahly, T.S.; Coffey, R.D.; Monegue,

H.J.; Randolph, J.H Efficacy of phytase in improving the

bioavailability of phosphorus in soybean meal and corn

soybean meal diets for pigs J Anim Sci 1993, 71, 1831

1840

6 Cromwell, G.L.; Traylor, S.L.; White, L.A.; Xavier, E.G.;

Lindemann, M.D.; Sauber, T.E.; Rice, D.W Effects of

low phytate corn and low oligosaccharide, low phytate

soybean meal in diets on performance, bone traits, and

P excretion by growing pigs J Anim Sci 2000, 78

(Suppl 2), 72 (abstract)

7 National Research Council Nutrient Requirements of Beef

Cattle, 7th Ed.; National Academy Press: Washington, DC,

1996

8 National Research Council Nutrient Requirements of

Dairy Cattle, 7th Ed.; National Academy Press: Wash

ington, DC, 2001

9 Wu, Z.; Satter, L.D.; Blohowiak, A.J.; Stauffacher, R.H.;

Wilson, J.H Milk production, estimated phosphorus

excretion and bone characteristics of dairy cows fed

different amounts of phosphorus for two or three years

J Dairy Sci 2001, 84, 1738 1748

10 Erickson, G.E.; Klopfenstein, T.J.; Milton, C.T.; Brink, D.;

Orth, M.W.; Whittet, K.M Phosphorus requirement of

finishing feedlot calves J Anim Sci 2002, 80, 1690

1695

11 Baker, D.H.; Han, Y Ideal amino acid profile for chicks during the first three weeks posthatching Poult Sci 1994,

73, 1441 1447

12 Allee, G.; Liu, H.; Spencer, J.D.; Touchette, K.J.; Frank, J.W Effect of Reducing Dietary Protein Level and Adding Amino Acids on Performance and Nitrogen Excretion of Early Finishing Barrows In Proceeding of the American Association of Swine Veterinarians; Amer ican Association of Swine Veterinarians: Perry, PA, 2001;

527 533

13 Erickson, G.E.; Klopfenstein, T.J.; Milton, C.T Dietary Protein Effects on Nitrogen Excretion and Volatilization in Open dirt Feedlots In Proceedings of the Eighth Interna tional Symposium on Animals, Agriculture and Food Processing Wastes; ASAE Press: St Joseph, MO, 2000;

204 297

14 Satter, L.D.; Klopfenstein, T.J.; Erickson, G.E The role of nutrition in reducing nutrient output from ruminants

J Anim Sci 2002, 80 (E Suppl 2), E143 E156

15 Klopfenstein, T.J.; Erickson, G.E Effects of manipulating protein and phosphorus nutrition of feedlot cattle on nutrient management and the environment J Anim Sci

2002, 80 (E Suppl 2), E106 E114

16 Wang, S.J.; Fox, D.G.; Cherney, D.J.; Chase, L.E.; Tedeschi, L.O Whole herd optimization with the Cornell net carbohydrate and protein system III Application of

an optimization model to evaluate alternatives to reduce nitrogen and phosphorus mass balance J Dairy Sci 2000,

83, 2160 2169

666 Nutrient Management: Diet Modification

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Nutrient Management: Water Quality/Use

J L Hatfield

United States Department of Agriculture, Agricultural Research Service, Ames, Iowa, U.S.A

INTRODUCTION

Animals generate a valuable source of nutrients in both

organic and inorganic forms Nutrients in manure can be a

valuable soil amendment; however, if manure is misused,

it can be a potential water quality problem Water quality

is a primary concern among environmental issues; manure

application is the focus of this article

MANURE NUTRIENTS

Nutrients vary among species, manure handling, and

storage systems as shown in Table 1 Nutrient content is

affected by species, diet, age, sex, manure storage system,

and length of time in storage Values shown in Table 1

illustrate the nutrient content in different manure storage

systems but do not represent the full range of variation

within a species or among manure storage systems

These data provide an indication of the variation

among species and the need for nutrient management

systems to consider animal production systems and

manure storage systems before making assumptions about

the best management system The goal in nutrient

management is to develop a system in which manure

nutrients may be applied to the soil to supply the crop

needs without being a potential environmental problem

WATER QUALITY CONCERNS

In nutrient management, water quality concerns focus on

phosphorus (P) and nitrate-nitrogen (NO3-N) Broadcast

manure on the soil surface provides for potential surface

runoff conditions, particularly when rain occurs shortly

after application In a 2001 study, broadcasting manure

resulted in the greatest potential for surface runoff of

soluble P.[2] Kleinman and Sharpley[3] compared

dis-solved reactive phosphorus from three manures at six rates

under simulated rainfall and found that dissolved reactive

phosphorus loss was related to runoff and manure

application rate Soluble P losses were a function of the

type of manure, the application rate, and soil type

Broadcast manure on the soil surface increases the

potential for surface runoff into nearby surface water

bodies In addition, surface runoff of manure may provide pathogens that are present in manure a pathway into nearby water bodies There are few studies of this problem and the evidence is insufficient to provide a set of factors that contribute to pathogen movement

Incorporation of manure into the soil greatly reduces the chances of surface runoff Tabbara[4] showed that incorporation of manure or fertilizer 24 hours before a heavy rainfall reduced both dissolved reactive P or total P concentrations by as much as 30% to 60% depending on the nutrient source and application rate The incorporation process moves P below the volume of soil eroded under high rainfall events To reduce potential surface losses of

P, manure should be incorporated on soils with intensive erosive rain, recent extensive tillage, or little or no surface residue Incorporation of manure will reduce the likeli-hood of surface runoff of P and protect surface water from excess P levels; however, the process of incorporating manure may increase the potential for sediment loss from the soil The development of management practices that protect soil from surface runoff will decrease potential losses of manure P into nearby water bodies

Incorporation of manure may lead to NO3-N leaching because nutrients placed below the surface mixing layer are in a soil volume where leaching of nutrients can occur

NO3-N present in the manure may be moved into deeper soil layers by soil water However, there is no evidence that this is a direct result of manure application Incorporation of manure changes the availability of nutrients in the soil profile Nutrients present in manure are in the organic form and the conversion into available forms is a function of biological activity and time in the soil profile Klausner et al.[5] developed a method to estimate the decay rate for organic nutrients from dairy manure that has worked well for this species over a range

of environmental conditions One of the challenges for manure management is to determine the temporal patterns

of nutrient availability from different manure types and species Jokela[6]showed that NO3-N levels were actually lower in soils treated with dairy manure compared to commercial fertilizer because of the slower release of

NO3-N from manure

Nutrient patterns in manured soils can lead to potential water quality problems; however, these can be managed through a proper rate of application and incorporation

DOI: 10.1081/E EAS 120019732

Published 2005 by Marcel Dekker, Inc All rights reserved.

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Water quality problems can be reduced through relatively

simple management practices that increase nutrient

availability to the crop and decrease the potential for

offsite movement through runoff or leaching

EFFECT OF MANURE ON SOIL PROPERTIES

RELATED TO WATER QUALITY

Addition of manure to soil causes changes in the soil

properties[7,8]that reduces the likelihood of water quality

problems Water infiltration rate, soil water-holding

capacity, cation exchange capacity, bulk density, organic

matter, biological activity, and plant availability of

nutrients are changed by manure additions These changes

required at least five years of manure additions to the

soil A positive impact on water quality is derived from

increased water infiltration rates and water storage

ca-pacity Surface runoff occurs in soils that quickly develop

a surface seal and ponding begins on the soil surface leading to the development of small rills that transport water along the surface Manure-amended soils have a larger infiltration rate and more rainfall can enter the soil before saturation occurs This change is not a direct ef-fect of manure addition but a combination of increased biological activity and organic materials that create a more stable soil particle that has a higher soil water content before becoming saturated The higher water-holding capacity of soil allows more absorption before the profile is saturated Eghball et al.[9] concluded that the increased intensity of rainfall could cause surface runoff but changes in the soil properties from manure could offset water quality problems

Addition of manure to soil not only changes the soil properties but also restores the soil to a higher level of soil productivity Freeze et al.[10] found that the applica-tion of manure to eroded soil was of greater benefit than application to noneroded soils Changes in soil

Table 1 Nutrient content in solid and liquid manure for different species and manure handling systems

Species

Dry matter %

Dry matter %

(From Ref 1.)

Fig 1 Conceptual diagram of nutrient flows in the MINAS systems for the Netherlands (Adapted from Ref 11.)

668 Nutrient Management: Water Quality/Use

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properties are more detectable in eroded soils These

effects of manure can be realized with all sources and

types of manure Often the water quality problems that

occur in agriculture are from soils that are in a

degrad-ed state and restoration of soil properties will benefit

the environment

NUTRIENT ACCOUNTING FROM

MANURE SOURCES

To achieve water quality goals and manure application

requires the proper amount of nutrients added to the soil to

supply crop requirements The components in a nutrient

budget are rates of crop removal, change in the soil

nutrient content, and amount supplied from manure In the

Netherlands, nutrient accounting systems have been

developed for livestock and cropping systems Ondersteijn

et al.[11] described the mineral accounting system

(MINAS) and provided a framework for nutrient

account-ing (Fig 1) Manure that is produced is accounted for

through the MINAS approach to ensure that both an

economic and environmental quality goal is achieved

Development of nutrient management guidelines for

producers to help guide their decisions can have a positive

impact on environmental quality

CONCLUSION

Nutrient management programs must have a positive

impact on water quality The challenge for producers is to

understand the nutrient balance in the soil and to reduce

the risk of surface runoff of manure The challenge for

science is to increase our understanding of the value of

manure in the soil and in the restoration of eroded soils to

a higher level of productivity Improved methods for

sampling manure to determine the nutrient content from

individual farms and for manure application that

incor-porates manure to reduce erosion and enhance the value of

manure on soil properties will benefit livestock, crop producers, and the environment

REFERENCES

1 MWPS (MidWest Plan Service) Manure Storages Ma nure Management System Series MWPS 18, Section 2 MidWest Plan Service Iowa State University: Ames, IA,

50011 3080, 2001

2 Zhao, S.L.; Gupta, S.C.; Huggins, D.R.; Moncrief, J.F Tillage and nutrient source effects on surface and subsurface water quality at corn planting J Environ Qual

2001, 30, 998 1008

3 Kleinman, P.J.A.; Sharpley, A.N Effect of broadcast manure on runoff phosphorus concentrations over succes sive rainfall events J Environ Qual 2003, 32, 1072 1081

4 Tabbara, H Phosphorus loss to runoff water twenty four hours after application of liquid swine manure or fertilizer

J Environ Qual 2003, 32, 1044 1052

5 Klausner, S.D.; Kanneganti, V.R.; Bouldin, D.R An approach for estimating a decay series for organic nitrogen

in animal manure Agron J 1994, 86, 897 903

6 Jokela, W.E Nitrogen fertilizer and dairy manure effects

on corn yield and soil nitrate Soil Sci Soc Am J 1992,

56, 148 154

7 Sommerfeldt, T.G.; Chang, C Changes in soil properties under annual applications of feedlot manure and different tillage practices Soil Sci Soc Am J 1985, 49, 983 987

8 Sommerfeldt, T.G.; Chang, C Soil water properties as affected by twelve annual applications of cattle feedlot manure Soil Sci Soc Am J 1987, 51, 7 9

9 Eghball, B.; Gilley, J.E.; Baltensperger, D.D.; Blumenthal, J.M Long term manure and fertilizer application effects on phosphorus and nitrogen in runoff Trans ASAE 2002, 45,

687 694

10 Freeze, B.S.; Webber, C.; Lindwall, C.W.; Dormaar, J.F Risk simulation of the economics of manure application to restore eroded wheat cropland Can J Soil Sci 1993, 87,

267 274

11 Ondersteijn, C.J.M.; Beldman, A.C.G.; Daatselaar, C.H.G.; Giesen, G.W.J.; Huirne, R.B.M The Dutch mineral accounting systems and the European nitrate directive: Implications for N and P management and farm perfor mance Agric Ecosyst Environ 2002, 92, 283 296

Nutrient Management: Water Quality/Use 669

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Nutrient Requirements: Carnivores

Duane E Ullrey

Michigan State University, East Lansing, Michigan, U.S.A

INTRODUCTION

Carnivores, broadly defined, sustain themselves by

feeding on vertebrate or invertebrate animal tissues, a

practice observed in both the animal and plant kingdoms

The Venus flytrap (Dionaea muscipula), one of over 500

carnivorous plant species, lives in humid, acidic bogs in

the Carolinas and, like most plants, acquires energy and

nutrients by photosynthesis and through the roots In this

environment, nitrogen and some mineral elements are in

short supply, and these needs are met by capturing insects

attracted to nectar in a specialized leafy trap, functioning

both as a mouth and stomach Animals, of course, do not

possess roots or the mechanisms of photosynthesis Thus,

energy and nutrient requirements of wild carnivorous

animals are acquired principally by consuming vertebrate

or invertebrate prey.[1,2]

Wilson[3] estimated there are about 4000 species of

extant mammals, 9000 of birds, 6300 of reptiles, 4200 of

amphibians, and 18,000 of fish and lower chordates The

nutrient requirements of these species are presumed to be

qualitatively similar, but quantitative nutrient

require-ments have been defined by the National Academy of

Sciences/National Research Council (NAS/NRC) only for

humans and a few domesticated or captive mammals,

birds, and fish Of the species with NRC-defined

require-ments, the cat, mink, tarsiers, rainbow trout, and salmon

are obligate carnivores The NRC also has defined the

nutrient requirements of the dog and fox, but these species

appear to be facultative carnivores and may consume

considerable vegetable matter

CARNIVOROUS MAMMALS

The immediate ancestors of the domestic cat (Felis catus)

were strictly carnivorous, and its needs have been the most

thoroughly studied of any of the obligate carnivores

Although commercial diets for cats may contain vegetable

matter, the nutrients and the amounts that must be present

reflect a long evolutionary dependence on a strictly

carnivorous diet The cat has a simple digestive system,

presumably because digestibility of natural prey tends to

be high, and there is no need for extended food retention

and microbial fermentation Due to its limited ability to

conserve nitrogen, the cat has a high protein requirement, and it converts only negligible amounts of tryptophan to niacin (neither ability is necessary when consuming whole prey) Requirements for blood glucose are met primarily

by gluconeogenesis rather than from dietary carbohydrate, and the cat has a high requirement for arginine for disposal of nitrogen via the urea cycle It requires taurine and arachidonic acid because of limited tissue synthesis (vertebrate prey provide adequate amounts), and it is unable to convert b-carotene (a plant provitamin) to vitamin A Vitamin D3 needs are met by diet because cutaneous concentrations of 7-dehydrocholesterol (provi-tamin D3) are insufficient to support vitamin D photobio-genesis Nutrient needs of the cat have been reviewed by the NRC,[4]and minimal requirements, adequate intakes, and recommended allowances have been published The NRC-recommended allowances for growth, maintenance, late gestation, and peak lactation are presented in Table 1 The mink (Mustela vison) eats small mammals, fish, frogs, crayfish, insects, worms, and birds in the wild Like the cat, its protein requirements are high 38% of dietary dry matter (DM) from weaning to 13 weeks of age, 22 26% for adult maintenance, 38% for gestation, and 46% for lactation.[5] Whether the mink shares the other unique metabolic features of the cat has not been determined

Tarsiers (Tarsius spp.) eat insects (beetles, ants, locusts, cicadas, cockroaches, mantids, moths) and sometimes small vertebrates in the wild Although the quantitative nutrient requirements of tarsiers have not been specifically defined, estimated adequate nutrient concentrations in dietary DM have been proposed.[6] When kept in captivity, tarsiers are often provided crickets

as a major food item Because crickets and other commercially available insects tend to be deficient in certain nutrients (particularly calcium, vitamin A, and vitamin D),[7]specifically formulated diets are offered to these insects for about 48 hours before feeding them to tarsiers so that the insects plus their gut contents will be nutritionally complete.[8–10]

Other obligate carnivorous mammals include felids such as lions, tigers, leopards, cheetahs, and jaguars Aquatic mammals such as dolphins, seals, sea lions, and walruses also are obligate carnivores, but little is known about their quantitative nutrient requirements

DOI: 10.1081/E EAS 120019733 Copyright D 2005 by Marcel Dekker, Inc All rights reserved.

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Table 1 Recommended nutrient allowances in dietary dry matter (DM) for domestic cats consuming diets containing 4 kcal of metabolizable energy per g of DM

Eicosapentaenoic and

docosahexaenoic acid, %

a

At least twice as much phenylalanine (or phenylalanine plus tyrosine) is required for maximal black hair color as for growth.

b

Recommended taurine allowances are lowest when diets are unprocessed (0.04% of DM) but are increased by extrusion (0.1% of DM) or canning (0.2%

of DM).

(Adapted from Ref 4, recommended allowances for growth of an 800 g kitten, maintenance or late gestation of a 4 kg adult cat, and lactation of a 4 kg queen with four kittens.)

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CARNIVOROUS BIRDS

The digestive systems of obligate carnivorous birds (such

as hawks and eagles), like their mammalian counterparts,

do not have compartments adapted for microbial

fermen-tation Relatively indigestible portions of prey, such as fur,

feathers, bones, fins, scales, shells, and exoskeletons, may

be separated from more digestible portions by the beak

prior to food ingestion Sometimes, this separation is

accomplished in the gizzard, followed by egestion of

indigestible matter out of the mouth, as in owls.[11]

Although the NRC[12] has defined the nutrient

require-ments of poultry, these species are principally

herbivo-rous Based on present metabolic evidence and the

composition of vertebrate and invertebrate prey, it seems

likely that nutrient needs of carnivorous birds are similar

to those of carnivorous mammals, with adjustments for

differences in reproductive strategy

CARNIVOROUS REPTILES

AND AMPHIBIANS

The long evolutionary association of snakes, crocodilians,

and some lizard families with subsistence on vertebrate

and invertebrate prey suggests that they are obligate

carnivores They tend to have simple gastrointestinal

systems as compared to herbivorous reptiles, although

there are adaptations related to the periodicity of feeding

and to unique characteristics of certain food items

Tortoises are chiefly herbivorous with a few that are

omnivorous Turtles tend to be omnivorous carnivorous

as juveniles and herbivorous or omnivorous as adults

although a few species are mostly carnivorous throughout

life.[13] Studies that define qualitative or quantitative

needs of reptiles are few, although protein and amino acid

needs of the hatchling green sea turtle (Chelonia mydas;

carnivorous as hatchlings, herbivorous as adults) have

been investigated Some studies suggest that young

red-eared slider turtles (Trachemys scripta elegans) and green

anoles (Anolis carolinensis) do not have an elevated

requirement for arginine (as does the cat), and addition of

taurine to a diet based on plant proteins does not improve

growth of young American alligators (Alligator

missis-sippiensis) Also, American alligators appear to convert

linoleic acid to arachidonic acid to some extent, although

rates may not be optimum for maximum growth.[1]When

a purified diet containing adequate tryptophan but no

niacin was administered weekly by stomach tube to bull

snakes (Pituophis melanoleucus sayi) for 132 days, no

signs of deficiency were seen, suggesting that either a

longer period of depletion is necessary to induce niacin

deficiency or metabolic conversion of tryptophan to niacin

may occur in this species.[14] Thus, if these reptiles are

indeed obligate carnivores, their nutrient needs seem to deviate from those of the cat

Most amphibians appear to be obligate carnivores.[13] Adult frogs and toads consume invertebrates and small vertebrates, although most species are herbivorous as larvae (tadpoles) and have a long, coiled intestine permitting them to digest plant matter At metamorphosis, the intestine is much shortened and the diet becomes strictly carnivorous Tadpoles of a few species are carnivorous and have a much shorter gut than do herbivorous tadpoles Salamanders and newts are carniv-orous both as larvae and as adults, feeding on insects, slugs, snails, and worms Caecilians (limbless, viviparous amphibians) prey on worms, termites, and orthopterans Metabolic features characteristic of carnivory have not been well studied in amphibians

CARNIVOROUS FISH Rainbow trout (Salmo gairdneri) and coho salmon (Oncorhynchus kirsutch) have protein requirements of

 40% of dietary DM for maximal growth of juveniles and have an absolute requirement for arginine They also lack the ability to synthesize niacin from tryptophan Gluco-neogenesis is important for provision of blood glucose, and essential fatty acid requirements include linoleic acid and eicosapentaenoic acid and/or docosahexaenoic acid.[15]

CONCLUSIONS Qualitative and quantitative nutrient requirements of obligate carnivores generally appear to reflect evolution-ary adaptations to the composition of ancestral diets

REFERENCES

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